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Feebates – Modeling

DEVELOPMENT OF OPTIONS FOR A VEHICLE FEEBATE IN CANADA

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4. MODELING OF FEEBATE OPTIONS

4.1 DESCRIPTION OF MODELS

Two

separate models were used in this analysis:

 

  • TransportCanada Variant of Greene et al. Vehicle Purchase Model. 

    This is a spreadsheet-based, nested multinomial logit,consumer choice model that estimates the effect of

    feebates on consumer purchasing behaviour and manufacturer

    investment in fuel economy technologies. Each individual

    vehicle model is included (830 in total North American

    market), as well as its purchase price and fuel economy.

    The model solves for fuel economy changes that maximize

    consumer surplus given a defined feebate. Consumer

    surplus is maximized in response to the feebate “price”

    by:

    • shiftingvehicle demand towards more fuel-efficient carsand reducing overall vehicle demand
    • inducingmanufacturers to maintain or improve market shareby improving fuel economy, and
    • providingfuel savings to the consumer through lower overallfuel consumption.
    The

    model produces aggregate national results for a

    single future year (15 years in the future), representing

    the new long-run equilibrium impact of the feebate.

    Transport Canada modified the US model to use aggregated

    2003 Canadian and US sales data, updated the technology

    cost curves based on a 2005 literature review (necessary

    to track manufacturer responses to the feebate),

    and added redesign thresholds provided by EEA. (These

    EEA redesign thresholds are used to determine if

    sales are adequate in Canada to induce manufacturers

    to make manufacturing investments that produce fuel

    economy improvements.)

    A key assumption in the model is how consumers respond

    to the price signal introduced by the feebate. The

    model used the following elasticity assumptions

    to model the price response of consumers:

     

    • -10@ market share of 15 percent within a class 
    • -5@ market share of 10 percent between classes 
    • -1.0for overall sales 
    Some

    limitations of these assumptions are discussed below.

     

  • NRCanVehicle Stock Model. This is a simple 

    representation of vehicle turnover and usage overa 15-year period. The model also incorporates the

    technology redesign schedule provided by EEA for the

    US Energy Information Administration in order to estimate

    the timing of technology investments. Outputs include

    the path of annual fuel savings and GHG emission reductions

    leading up to the fifteenth year.

4.2 BASE CASE AND ASSUMPTIONSTo

isolate the effect of the feebate, a base case is assessed.

This case is generated by the model and based on allowing

consumer and manufacturer behaviour to evolve naturally

in response to the availability of cost saving-technology

with no feebate. The base case has not been calibrated

to NRCan’s reference case and it does not incorporate

macroeconomic or demographic factors. However, in evaluating

the incremental impact of feebates, these are not major

limitations.

The

key assumptions that remain constant for all scenarios

are:

 

  • Asingle fuel-efficiency cost curve for each class (providedby EEA)
  • 2000minimum threshold for redesign of import vehicles 
  • 20,000minimum threshold for redesign of domestic vehicles 
  • Vehiclelife of 15 years 
  • Averageyearly distance traveled of 23,500 km, declining 4percent per year
  • 15percent adjustment of fuel consumption rating to approximateon-road conditions
  • 23percent rebound effect (where decreased fuel costsinduce more driving, thus negating a portion of the

    feebate gains)

  • 10percent discount rate. 

4.3

LIMITATIONS

Like

all modeling exercises, the current one is a crude approximation

of reality designed to provide policy guidance. While

the model has limitations that we highlight below, it

is our view that the model can be used to inform policy.

Limitations include:

 

  • Decisionbasis. In the real world, manufacturers 

    would redesign based on a number of complex considerationsand consumers would be driven by a variety of considerations

    that are not easily represented by a simple elasticity

    function. In this simulation, the model assumes that

    manufacturers redesign their vehicles to maintain

    market share and not to maximize profits. Similarly,

    societal costs may be fairly represented by consumer

    surplus changes, but it is not possible to estimate

    the share of the burden that would fall on producers

    and not be passed on to consumers.

  • Airquality benefits. Important co-benefits 

    from reduced fuel consumption like improved air quality,a reduction in adverse health outcomes and the monetary

    value of those outcomes are also not modeled.

  • Valuationof fuel savings. A central assumption 

    of the model is that consumers undervalue fuel savings.A key limitation is that there is no data on the extent

    to which this is true of Canadian consumers. As a

    result, we use the same assumption as Greene et al.

    (three years undiscounted) and we undertake a sensitivity

    analysis by examining the effect of assuming that

    consumers already fully value fuel savings. To the

    extent that consumers do undervalue fuel savings,

    a feebate would be justified on efficiency grounds

    alone, with carbon mitigation benefits additive.

  • Consumerelasticities. These values determine 

    the extent to which consumers respond to price signals.Greene et al. used short-run elasticities, which are

    assumed to vary with make/model market shares, but

    are not estimated by manufacturer or vehicle class.

    Given the function used, classes with larger market

    shares have smaller elasticities, whereas models with

    small market shares have high elasticities (in some

    cases, unrealistically high). Furthermore, cross-price

    elasticities are not differentiated by make/model

    or class. This means that consumers diverted from

    buying a large SUV are assumed to be equally likely

    to buy a subcompact as a minivan or mid-size SUV.

    It also means that cross-price elasticities are higher

    across the board for classes with large market shares;

    this issue matters more for Canada, since the market

    shares are less evenly distributed than in the US.

    Since there is no comparable data on Canadian elasticities,

    our approach has been to use the Greene et al. elasticities

    but to halve them, as a way of approximating long-run

    responses and to mitigate some of the effects described

    above. We also undertake a sensitivity analysis by

    examining the effects of assuming the full elasticities

    prescribed by Greene et al.

  • Staticdesigns. The model uses a database of 

    vehicles, which is based on 2003 models and assumesno changes in makes and models over the 15-year period.

    This is unrealistic but neutral in terms of costs.

    Furthermore the model uses a static technology cost

    curve that assumes no progress in available fuel economy

    technologies over the period—this assumption

    tends to overestimate costs. Finally, the model assumes

    that all technology investments are used to improve

    fuel economy and that weight and performance remain

    constant. (Given past experience, this tends to overestimate

    the fuel economy effectiveness of the investments.)

  • Hybridand diesel technologies are not included. 

    As discussed in Section 2, hybrids and diesels areexpected to play a significant role in improving fuel

    economy. Unfortunately the current version of the

    model lacks the information necessary to include these

    options. (Our understanding is that Transport Canada

    is working to add them to the model soon.) As a result,

    the model overestimates costs and underestimates fuel

    economy gains.

  • Effectson used vehicle markets are not modeled. 

    As discussed in Section 2, the used vehicle marketrepresents more than half of vehicle sales. If the

    price of certain models rises because of feebates,

    it is likely that some of the demand will be filled

    from the used vehicle market. However, the model assumes

    that consumers primarily respond by shifting purchases

    to other new vehicles. As a result, the effectiveness

    of fuel economy gains is overestimated.

  • Thresholdapproach to redesign. The cost curve 

    approach does not account for economies of scale beyondthe pre-set threshold, as the thresholds are only

    set to limit the access to technology in a Canadian-only

    scenario.

  • Spillovereffects of unilateral Canadian policy. 

    The model assumes that unilateral Canadian policieshave no effect on US policy. Thus any spillover effects

    that might occur are discounted. For example, should

    Canadian policies increase the potential for voluntary

    or mandatory fuel economy improvements in the US,

    the effect of this on the overall size of the market

    for redesign is not included. (As a result, costs

    are potentially overestimated and effectiveness is

    underestimated.)

  • Reboundeffect. “Rebound” refers 

    to the increase in distance travelled that accompaniesreduced driving expenses (in this case, fuel savings).

    The model assumes a rebound effect of 23 percent—meaning

    23 percent of fuel savings are lost to this effect—based

    on research of past experience in the US. The potential

    future rebound effect in Canada has not been studied,

    but 23 percent almost certainly overestimates the

    effect and therefore underestimates the GHG savings.

4.4

SCENARIOS

The

primary purpose of the modeling is to explore the effects

of various feebate options. In this respect, the model

is primarily designed to examine the effects of varying

rate designs as opposed to implementation options, such

as approaches to revenue neutrality, phase-in periods,

or annual feebates at vehicle registration. As well,

the model is designed to use fuel consumption as the

rate basis.

 

Thus,

our scenarios are selected to include variations on

the following options:

 

  • Formof the function: Fully linear, $5,000 cap, or zerofeebate within 1.0 litre per 100 km of pivot (deadband)
  • Rate:$250, 500, or $1000 per litre per 100 km 
  • Numberof classes: single, car and truck, or 11 classes. 
A

secondary purpose of the modeling is to examine the

sensitivity of the results to differences in key assumptions.

In this respect, the following alternatives are considered:

 

  • Elasticities
    • Baseassumption – represents long-run elasticities(i.e. half of the values used by Greene et al.

      presented above)

      • -5@ market share of 1.5 percent within a class 
      • -2.5@ market share of 10 percent between classes 
      • -0.5for overall sales 
    • Sensitivityanalysis for double these figures (i.e. the fullvalues used by Greene et al.).
  • PolicyScope 
    • Baseassumption: feebates are implemented in Canadaonly
    • Sensitivityanalysis for Canada–US policy. 
  • ConsumerPerception of Value of Fuel Savings 
    • Baseassumption: three years of undiscounted savings 
    • Sensitivityanalysis for fuel discounted valuation. 
  • FuelPrice 
    • Baseassumption: C$0.90 per litre 
    • Sensitivityanalysis at C$1.20 per litre. 
These

alternative options and assumptions are grouped into

12 scenarios, as shown in Table 4.1.

 

Table 4.1: Specification of Scenarios

No.

Rate (C$/l/100km)

Classes

Caps or Plateaus

Elasticities

Jurisdictions

Valuation of Fuel Savings
Fuel Price $/l

1

Base

Case

N/A

N/A

50%

of Greene

Canada

– US

3

years, undiscounted

0.90

2

$250

Single

No

50%

of Greene

Canada

only

3

years, undiscounted

0.90

3

$500

Single

No

50%

of Greene

Canada

only

3

years, undiscounted

0.90

4

$1,000

Single

No

50%

of Greene

Canada

only

3

years, undiscounted

0.90

5

$500

Single

No

50%

of Greene

Canada

– US

3

years, undiscounted

0.90

6

$500

Single

Cap

at $5,000

50%

of Greene

Canada

only

3

years, undiscounted

0.90

7

$500

Single

Zero

within 1.0l/100km of pivot

50%

of Greene

Canada

only

3

years, undiscounted

0.90

8

$500

Separate

cars & trucks

No

50%

of Greene

Canada

only

3

years, undiscounted

0.90

9

$500

11

classes

No

50%

of Greene

Canada

only

3

years, undiscounted

0.90

10

$500

Single

No

50%

of Greene

Canada

only

3

years, undiscounted

0.90

11

$500

Single

No

50%

of Greene

Canada

only

3

years, undiscounted

0.90

12

$500

Single

No

50%

of Greene

Canada

only

3

years, undiscounted

1.20

4.5

 

RESULTS

Appendix

B contains detailed result for each of the scenarios.

Selected results are presented in Table 4.2.

Note that Scenario 7 could not be modeled because

of problems with the specification of the discontinuity.

Table

4.2: Scenario Results

 

Scenario
Total Transfer ($M)
Fuel Economy (l/100km) 2018
Unval. Fuel Savings ($M)
GHG Emission Reduction (Mt)
Societal Cost ($M)*Benefit shown as neg.
Sales (2010)

#

Policy

Options

Assumptions

2010

Cars

Trucks

2018

2018

2003-2018

2010

2018

2003-2018

Total

Change (#veh.)

Big

3 (%)

Other

(%)

Cars

(%)

Trucks

(%)

Avg.

Car Price ($)

Avg.

Truck Price ($)

1

Base

Case

First

3 yrs valuation

Base Elasticities

0

7.1

9.8

0

0

0

0

0

0

0

62

38

56

44

24,600

32,600

2

$250/l/100

km

Canada

only

First 3 yrs valuation

Base Elasticities

290

6.9

9.7

180

1.5

13

(80)

(180)

(540)

(260)

61

39

58

42

24,200

32,500

3

$500/l/100

km

570

6.8

9.5

370

3.0

26

(120)

(310)

(800)

(1,200)

60

40

59

41

23,800

32,400

4

$1000/l/100

km

1,100

6.5

9.2

760

6.2

53

(90)

(460)

(460)

(6,300)

58

42

62

38

23,100

32,200

5

$500/l/100

km

North

America

550

6.4

8.8

730

6.0

42

(160)

(650)

(1,340)

(1,800)

60

40

59

41

23,900

32,600

6

$500/l/100km

Cap@$5,000

Canada

only

First 3 yrs valuation

Base Elasticities

570

6.8

9.5

370

3.0

26

(120)

(310)

(800)

(1,200)

60

40

59

41

23,800

32,400

8

$500/l/100km

Sep. Cars & Trucks

450

6.8

9.5

250

2.1

16

(70)

(220)

(480)

(860)

61

39

56

44

23,800

31,400

9

$500/l/100km

11 Classes

280

6.8

9.6

200

1.6

12

(50)

(180)

(380)

(520)

61

39

56

44

23,900

32,400

10

$500/l/100km

Full

Valuation

590

6.6

9.2

0

3.0

26

20

(20)

292

(47))

61

39

58

42

23,700

32,500

11

$500/l/100km

Double

Elasticities

560

6.7

9.3

1,200

5.4

49

(540)

(1,070)

(3,540)

(5,700)

58

42

62

38

23,000

32,100

12

$500/l/100km

$1.20/l

580

6.7

9.4

400

2.4

21

(160)

(360)

(990)

(30)

60

40

59

41

23,700

32,400

4.6OBSERVATIONS

The

scenarios provide a basis for several observations:

  • GeneralObservations. The most significant findingsare:
    • Mostscenarios result in significant fuel savingsand GHG reductions.
    • Mostscenarios produce a net benefit—meaningfrom a societal perspective the benefits

      are greater than the costs—mostly

      in the form of unvalued fuel savings.

    • Incontrast with Greene’s US experience,most scenarios produce a more significant

      shift in sales (although technology still

      accounts for more than two thirds of the

      improvement). As a result, the average

      cost of vehicles is slightly lower and

      combined with slightly lower sales; total

      revenues are reduced by approximately

      $1.5 billion per year (approximately 4

      percent).

  • Effectof Rate Change. See Table 4.3. 

    The key observations are: 

    • Fueleconomy improves and therefore GHG reductionsincrease relatively linearly with an increasing

      feebate rate.

    • Theshift in sales also increases linearly. 
    • Netbenefits are positive for all rates butlevel off between $500 and $1000.
Table

4.3: Effect of Rate Change

 

Scenario

Change in GHG (Mt)
Total Societal Benefit ($M)
Change in Car Share

$250/l/100km

-13

540

1.6%

$500/l/100km

-26

790

3.1%

$1000/l/100km

-53

460

6.1%

  • Cap& Deadband. The key observations 

    are: 

    • Acap removes incentives for highly inefficientvehicles to improve, since they just pay

      a fixed fee. It also diminishes incentives

      to shift away from those vehicles.

      • A$5000 cap has no significant effect:only one vehicle (Ferrari Enzo) would

        be above this threshold.

      • Onlyone other (Chevrolet Silverado) wouldbe above $4000.
      • Only15 models out of 800 would be above$3000.
    • Adeadband removes incentives to improvefuel economy for vehicles near the pivot

      point.

      • Thus,reductions are fewer, and shiftingto more efficient vehicles is distorted.
      • Unfortunately,the model was unable to simulate thiseffect correctly.
  • ConsumerValuation of Fuel Savings. See 

    Table 4.4. The key observations are: 

    • AtC$0.90 per litre the full discounted valueof reducing fuel consumption by 1.0 per

      litre per 100 km would be $1700. If we

      assume that consumers only value three

      years, or $700, feebates provide a way

      to compensate for this. Thus, feebates

      up to $1000 per litre per 100 km should

      be cost-effective. Results are consistent

      with this expectation:

      • Thetotal surplus (net benefit) improvesas the feebate rise.
      • Allscenarios up to $1000 have benefitsinstead of costs.
      • Forrates higher than $1000, the costswould outweigh the benefits on the

        margin.

    • Fullvaluation means that the base case ismore advantageous and that the benefits

      of feebates are correspondingly reduced.

      Fuel economy still improves but there

      is a net cost per tonne for GHGs.

Table

4.4: Effect of Consumer Valuation Assumption

 

 
Baseline FC in 2018 (l/100km)
Average FC in 2018 (l/100km)
Change in Consumer Surplus ($M)
Unvalued Fuel Savings ($M)
Total Societal Benefit ($M)
$500/l/100km,

3yr valuation

8.3

7.9

-510

1300

790

$500/l/100km,

full valuation

8.1

7.7

-290

 

-290

  • Segmentation.See Table 4.5. The key observations are: 
    • Differentiatingpivot points means a lower fee or evena rebate as larger vehicles are assessed

      only against their cohorts. This discourages

      shifting to smaller vehicles (less change

      in market shares) and means less improvement

      in consumer surplus and fewer GHG reductions.

      Results are consistent with this expectation.

      • Segmentationof cars and trucks reduces fuel economy,GHG reductions and benefits, while

        virtually eliminating the shift between

        cars and trucks (and reducing the

        shift between manufacturers).

      • Goingto 11 classes has little additionaleffect.
Table

4.5: Effect of Segmentation

 

Scenario

Change in GHG (Mt)
Total Societal Benefit ($M)
Change in Car Share
$500/l/100km,

1 pivot

-26

790

3.11%

$500/l/100km,

2 pivots

-16

480

0.02%

$500/l/100km,

11 pivots

-12

380

0.00%

  • PolicyIntegration with US. See Table 

    4.6. The key observations are: 

    • Witha unilateral policy, not all makes/modelsmeet the threshold for retooling. Fuel

      economy is then determined by the average

      North American willingness to pay (WTP)

      and a Canadian feebate raises this WTP

      according to the Canadian market share.

    • WithNorth American implementation, all vehiclesimprove according to the full change in

      consumer willingness to pay. As a result,

      GHG reductions are larger and the change

      in Canadian surplus is larger. An integrated

      North American feebate doubles the GHG

      reductions and benefits for the same shift

      in sales.

Table

4.6: Effect of Policy Integration with the U.S.

 

Scenario

Change in GHG (Mt)

 

Total Societal Benefit ($M)
Change in Car Share
$500/l/100km,

Canada

-26

790

2.76%

$500/l/100km,

North America

-42

1,340

2.48%

  • Elasticities.See Table 4.7. The key observations are: 
    • Elasticitiesdetermine the effects on total sales andshift in the fleet mix. Greene’s

      original elasticities represented short-run

      responses; to better reflect the available

      information on long-run responses, we

      halved them to get our baseline elasticities.

      As a result, the baseline elasticities

      yield more conservative estimates of the

      benefits to consumers, but also predict

      smaller sales shifts.

    • WithGreene’s original elasticities,consumers are more sensitive to price

      changes. As a result, the sales mix changes

      more easily but policies are less costly,

      since consumers take greater advantage

      of the option to purchase other vehicle

      types. This doubles the size of the sales

      shifts and the GHG reductions. At the

      same time, the change in surplus is five

      times greater.

Table

4.7: Effect of Elasticity Assumptions

 

Scenario

Change in GHG (Mt)
Change in Consumer Surplus ($M)
Unvalued Fuel Savings ($M)
Total Societal Benefit ($M)

 

Change in Car Share, 2018
Change in Sales, 2018
$500/l/100km

Baseline Elasticities

-26

-510

1,300

790

2.8%

-0.1%

$500/l/100km

Double Elasticities

-49

-680

4,580

3,900

5.7%

-0.4%

  • Priceof Fuel. See Table 4.8. The 

    key observations are: 

    • Ahigher fuel price means that there ismore incentive for fuel economy present

      in the base case. Thus, the incremental

      of the feebate on fuel and GHG savings

      is reduced (by about 20 percent).

    • Onthe other hand, the unvalued fuel savingsare worth more so the overall benefit

      is higher and the benefit per tonne is

      greater (almost $50 per tonne).

    • Theprice of fuel has little impact on thesales mix.
Table

4.8: Effect of Fuel Price

 

Scenario

Change in GHG (Mt)
Change in Consumer Surplus ($M)
Unvalued Fuel Savings ($M)
Total Societal Benefit ($M)
Change in Car Share, 2018
$500/l/100km

Fuel @ $0.90/litre

-26

-510

1,300

790

2.8%

$500/l/100km

Fuel @ $1.20/litre

-49

-680

4,580

3,900

2.9%

4.7

IMPLICATIONS

  • Modelresults are subject to the limitations andassumptions described above. The main

     

    value of the model is to assist in understandingthe relationships between inputs and various

    indicators of environmental effectiveness,

    economic efficiency, etc. Thus, although the

    results are considered directionally valid,

    individual values should be treated with caution.

  • Someimplications are clear and relatively robust.Notwithstanding modeling limitations

     

    and assumptions, there are a number of findingsderived from a logical understanding of the

    mechanisms at work and, therefore, not likely

    to be in doubt. These findings are:

    • Feebateswill encourage additional investment infuel-efficiency technology and shift the

      market towards more fuel-efficient vehicles

      (trucks to cars, large cars to small cars,

      more fuel-efficient cars in the same class).

    • Overtime, this will improve the fuel efficiencyof the vehicle stock and will reduce GHG

      emissions.

    • Theinvestment in fuel-efficiency technologywill raise the cost of individual vehicles

      and reduce consumer surplus accordingly.

    • Tothe extent that consumers undervalue fuelsavings, feebates will capture savings

      that would otherwise not have been realized.

      If the undervaluation is significant,

      over the life of the vehicle fuel savings

      are likely to exceed the added cost to

      vehicles, resulting in a net economic

      benefit to society.

    • Higherprices will depress vehicles sales. 
    • Theshift towards more fuel-efficient vehicleswill also reduce overall revenues.
    • Ina single-class feebate, GM, Ford, andDCX will lose additional market share

      and will bear a disproportionate share

      of the adjustment costs. This could be

      alleviated by adopting separate classes

      for trucks and cars, though this would

      reduce GHG savings and economic benefits.

    • Theextent of the shifts is determined bythe elasticities of demand. If elasticities

      are greater than expected, the environmental

      and economic benefits will be greater

      but so will the adjustment costs. Conversely,

      if elasticities are less than expected,

      the environmental and economic benefits

      will be reduced, as will the burden on

      manufacturers.

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